Habitat and Biology
Climatic zone: Temperate. Bottom type: Soft bottom. Depth zone: Shelf 50 200m. Horizontal distribution: Neritic; Littoral. Vertical distribution: Demersal/Benthic.
Geographical Distribution
Jurisdictional distribution: Straddling between High Seas and EEZ
Resource Structure
Considered a single stock: Aq Res Struct
Exploitation
Mullus barbatus is exploited by trawl and artisanal fisheries fleets in GSA06, although small gears (trammel nets and gillnets) account only for 5% of their total landings (Demestre et al., 1997). Trawl fisheries developed along the continental shelf and upper slope are multi-species. Small vessels operate almost exclusively on the continental shelf targeting on red mullets, octopus, cuttlefish and sea breams. Medium and large vessels usually operate on the slope areas targeting on hake and decapod crustaceans, but some of these units can also operate on the continental shelf depending on the season (e.g. red mullet is more intensively exploited from September to November; Martín et al., 1999), the weather conditions or market prices. Landings of
M. barbatus increased continuously from the earliest 1970's until 1982. From this year until now a general decreasing trend with fluctuations is observed. Important fractions (28% of individuals) of
M. barbatus are under the minimum legal size. The total number of boats (trawl fleet) in the GSA06 has been reduced 30% from 1998.
Assessment
Data
Total annual landings 1995-2010. Annual catch in numbers by size class. Abundance index from commercial fleet and MEDITS surveys. Growth parameters are those obtained by Demestre et al. 1997. Length-weight relationships and oogive of maturity were obtained within the framework of the Spanish Data Collection Programme. The vector of natural mortality-at age was obtained from Caddy´s (1991) formula using the PROBIOM Excel spreadsheet (Abella et al. 1997).
Assessment Model
Type: Age-structured
Extended Survivors Analysis (XSA)
Results
PopulationSpawning Stock Biomass (SSB): 686 t
Fishing mortality ratesF
0-2 = 0.8
Assessment Model
Type: Others
Predictive model
Yield per Recruit (Y/R)
Results
Y/R results
| |
Total |
| Current Y/R |
11.37 |
| Maximum Y/R |
11.53 |
| Y/R0.1 |
9.93 |
| Fmax |
0.348 |
| F0.1 |
0.196 |
| Current B/R |
33.1 |
| Maximum B/R |
55.96 |
| B/R0.1 |
77.48 |
| Fcurrent |
0.73 |
Overall Assessment Results
The stock is in overfishing status and in low level of abundance.
Scientific Advice
For scientific researchTo improve biological and growth parameters;
Besides on-board sampling, sampling at port is also needed.
For management considerationTo reduce the fishing effort 70%;
More effective control in shelf areas above 50 m depth should reduce the catch of small individuals under the minimum legal size;
Transition analysis indicates that a 24% increase in Y/R is expected with the square mesh in the cod-end. A 32% increase in Y/R is expected with both the square mesh and a 20% decrease in fishing effort and a 44% increase in Y/R is expected with a 40% decrease in fishing effort and the use of the square mesh, but a close supervision of the observance of this measure is needed.
Biological State and Trend
Exploitation state: OverexploitedExploitation rate: High fishing mortality
Abundance level: Low abundance
Catch in number of individuals are based on younger ages (0 and 1). Average F for ages 0-2 shows a general decreasing trend over the studied period reflecting the continuous reduction observed in the fleet. Recruitment shows a slight decreasing trend, being under the average of the whole period in the last two years. There isn't any trend in the total biomass whereas SSB shows a slight increasing trend.
Source of information
Report of the Working Group on Stock Assessment of Demersal Species. FAO-GFCM Chania, Crete (Greece) 24-29 October 2011. 2011 FAO

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